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ARCHIVED REPORTS_XR0005595
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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1985
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2900 - Site Mitigation Program
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PR0543949
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ARCHIVED REPORTS_XR0005595
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Last modified
7/27/2020 5:51:41 PM
Creation date
7/27/2020 4:26:48 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0005595
RECORD_ID
PR0543949
PE
2960
FACILITY_ID
FA0024995
FACILITY_NAME
TED PETERS TRUCKING COMPANY
STREET_NUMBER
1985
Direction
W
STREET_NAME
YOSEMITE
STREET_TYPE
AVE
City
MANTECA
Zip
95337
APN
20014019
CURRENT_STATUS
01
SITE_LOCATION
1985 W YOSEMITE AVE
P_LOCATION
04
QC Status
Approved
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EHD - Public
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Geolagccal Tec"Cs 1AC Page 5 <br /> GW Monitonng Report <br /> Ted Peters-AST <br /> Project No 701 2 <br /> May 15, 2003 <br /> 30 FINDINGS AND DISCUSSION <br /> ' The results of the groundwater sample analyses show the following <br /> • Groundwater samples from three of the five AST monitoring wells (MW-4, MW-6 and <br /> MW-7) reveal the presence of TPH-G or gasoline constituents Well MW-5 probably <br /> contains TPH-G but the detection limits are elevated due to the presence of high levels <br /> of TPH-D <br /> • Well MW-5 contained TPH-D at 212,000 µg/l, which is the highest recorded amount <br /> ' thus far in the investigation <br /> • A heavy sheen of product was noted in MW-5 for this event This well has contained <br /> free product during previous events <br /> • Well MW-8 contained trace BTEX constituents at concentrations dust above the <br /> laboratory reporting limits for the January 2003 event This was the first time since the <br /> well's installation in March 2001 that it has contained detectable contamination It has <br /> now returned to non-detectable levels <br /> 0 Oxidation-Reduction Potential (ORP) and Dissolved Oxygen (DO) measurements <br /> (Table 3) suggest that all of the AST wells are in the core of the contamination plume or <br /> ' are immediately down gradient of the plume Negative ORP values and low DO values <br /> indicate that the wells are within the halo of reaction depleted water caused by <br /> biodegradation of the contaminants For the April 2, 2003 event, three wells MW-5, <br /> MW-6 and MW-7 had negative ORP values MW-4 is in the vicinity of the primary <br /> contamination sources (diesel ASTs) and MW-8 is perpendicular to gradient <br /> • Figure 4 illustrates TPH-G concentrations in groundwater in the vicinity of the former <br /> ' ASTs The highest level of TPH-G detected is in well MW-4, which is different from <br /> past events, which showed that MW-7 on the northwest side of the parcel had the <br /> highest concentrations Well MW-5 has previously contained the highest levels of TPH- <br /> G but contained free product sheen for this event <br /> ' • Figure 5 illustrates TPH-D concentrations in groundwater in the vicinity of the former <br /> ASTs Well MW-5 contained free product sheen GTI's previous GeoProbe <br /> investigation revealed that the diesel contamination is limited to the area of former ASTs <br /> ' and associated dispensers <br /> 4 0 CONCLUSIONS & RECOMMENDATIONS <br /> Conclusions <br /> I Groundwater flow is predominantly to the northwest for both the AST and UST sites on <br /> this property GTI believes that previous southwesterly directions noted in the AST area <br /> are anomalous based on the presence of free product in MW-5 and/or the spatial <br /> orientation of the wells <br /> ' 2 TPH-G, TPH-D or volatile organic compounds are present in four of five groundwater <br /> monitoring wells <br /> 3 The TPH-G concentrations exhibit a decreasing trend in the downgradient well MW-7 <br /> ' Figure 6 Well MW-7 TPH-G & Benzene versus Elevation illustrates this situation <br /> 4 The methylene chloride found in MW-4 through MW-7 is believed to be a lab <br /> l contaminant and not present in groundwater aquifer <br />
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